The ARCHY code, and permafrost carbon Bryan Travis Los Alamos Irena Ossola Columbia University/LANL February 9, 2010 NCAR, Boulder, CO
The ARCHY code, and permafrost carbon
Bryan Travis Los Alamos
Irena OssolaColumbia University/LANL
February 9, 2010NCAR, Boulder, CO
Hydrology - surface snow, water (hillslope runoff, river routing)
Ecology - plants
Climate - atmosphere, clouds
Precip(t) snow/rain
Runoff, hydrographs, bank stability
Active layer - microbes …, emissions
T(t), s.i., albedo
Outflow to oceans, sediment, fresh water
Extreme events, fires
subsurface energy and fluid flow, permafrost dynamics
Coupled Dynamics of Arctic Regions
evap
SPA
HRR
ARCHY
ARCHY/MAGHNUM model
1-D, 2-D, 3-D + time; Cartesian, cylindrical coordinates; integrated finite differences; MPI version this year
Two-phase flow; mass and energy conservation equations + Darcy’s Law; water (single phase), water + air/vapor (two phase coupled), ice, melting/thawing, latent heat
Variable properties (H2O eos, permeability, porosity, thermal properties, spatial and temporal variation, feedbacks)
Chemistry – one version coupled to PHREEQC; solute transport, precipitation/dissolution, feedback to porosity and permeability
Microbial kinetics module – multiple Monod, multiple species including aerobic and anaerobic; C-N cycles
Checks and tests
• Analytic solutions for some simple cases• Diffusion with phase change (Stefan problems)• Single phase flow – steady solutions, comparisons to
other codes for transient cases• Similarity solutions for 2-phase flow• Comparisons to other numerical solutions (e.g., Grimm
& McSween; McKenzie et al)• Comparisons to experiments (e.g., McGraw)• Predecessor codes (MAGHNUM, TRACRI, …) have
been used and tested for a variety of applications
Microbial Activity
Bacterial respiration can convert large amounts organic carbon in soil to carbon dioxide andmethane. Several variables drive the response of microbial activity. Emission levels are sensitive tosoil composition, temperature, moisture and nutrients (such as nitrates and phosphates) andmicrobial community make-up.
-Methanogens: Bacteria that produce methane under anaerobic conditions from the breakdown of organic carbon.
Reaction: CH3COOH --> (1-x) CH4 + (1-x) CO2 + 2x Man where dMan/dt = d4R2 - λanMan
-Aerobes: Bacteria that utilize oxygen to metabolize organic carbon
Reaction: CH3COOH + (2-x) O2 --> where dMae/dt = d2R1 - λaeM
(2-x) CO2 + (2-x) H2O + x Mae
-Methanotrophs: Bacteria that consume methane as their predominant source of carbon and energy.
Reaction: CH4 + (2-x) O2 --> (1-x) CO2 + (2-x) H2O + x Mt where dMt/dt = d5R3 - λtMt
Carbon: Aerobic: R1 = k1(T) Mae [O2/(Ko2 + O2)][C/(KC+C)]
Anaerobic: R2 = k2(T) Man [I/(I + O2)][C/(KIC+C)]
Methanotrophic: R3 = k3(T) Mt [O2/(Ko2 + O2)][CH4/(KCH4+CH4)]
CO2: dCO2/dt = aR1 + bR2 + c(b3R3)
CH4: dCH4/dt = b2R2 - b3R3
O2: dO2/dt = -a2R1 - d3R3
-The various coefficients in the equations are determined from stoichiometry and experimental data.
Consumption Rates
Arctic Distribution of Permafrost and Borehole MeasurementsCourtesy of : http://www.gtnp.org/location_e.html
Measurements of temperature and CH4 and TOC concentrations vs depth at a Siberian site. Inthe top soil, low water level leads to oxic conditions and a limited methane accumulation due totransformation of methane by methanotrophs. At greater depths, methane accumulates fromanaerobic microbe activity. We are using databases of In situ data to calibrate our model.
Data from: S. Liebner, K. Rublack, T. Stuehrmann, and D. Wagner, 2009. Diversity of Aerobic Methanotrophic Bacteria in a Permafrost Active Layer Soil of the Lena Delta, Siberia
Example model domain
30 m
10 m
Q = 60 mW/m2
Porosity and permeability assumed randomly distributed; pores are water or ice-filled
HH
H = heater location; part of study is to see how different heater configurations affect permafrost distribution
Initial T = -5 C
Heat transport, melting/thawing, fluid flow
Ice (l) and Temperature (r) distributions - August
A z-t profile of sample ARCHY simulation of microbial species activity(aerobes, anaerobes, methanotrophs) in spring to summer
Plans for Model
• Comparison to soil data (CO2, CH4 soil measurements, fluxes)
• Study interactions between physical and biological factors
• Couple to surface vegetation and roots model, e.g., SPA
• Sensitivity analysis – ranking of importance• Prediction of responses to climate changes